Federal Register: June 3, 2010 (Volume 75, Number 106)

DOCID: fr03jn10-14 FR Doc 2010-11974

ENVIRONMENTAL PROTECTION AGENCY

U.S. Citizenship and Immigration Services

CFR Citation: 40 CFR Parts 51, 52, 70, et al.

RIN ID: RIN 2060-AP86

EPA ID: [EPA-HQ-OAR-2009-0517; FRL-9152-8]

NOTICE: Part II

DOCID: fr03jn10-14

DOCUMENT ACTION: Final rule.

SUBJECT CATEGORY:

Prevention of Significant Deterioration and Title V Greenhouse Gas Tailoring Rule

DATES: This action is effective on August 2, 2010.

DOCUMENT SUMMARY:

EPA is tailoring the applicability criteria that determine which stationary sources and modification projects become subject to permitting requirements for greenhouse gas (GHG) emissions under the Prevention of Significant Deterioration (PSD) and title V programs of the Clean Air Act (CAA or Act). This rulemaking is necessary because without it PSD and title V requirements would apply, as of January 2, 2011, at the 100 or 250 tons per year (tpy) levels provided under the CAA, greatly increasing the number of required permits, imposing undue costs on small sources, overwhelming the resources of permitting authorities, and severely impairing the functioning of the programs. EPA is relieving these resource burdens by phasing in the applicability of these programs to GHG sources, starting with the largest GHG emitters. This rule establishes two initial steps of the phasein. The rule also commits the agency to take certain actions on future steps addressing smaller sources, but excludes certain smaller sources from PSD and title V permitting for GHG emissions until at least April 30, 2016.

SUMMARY:

Environmental Protection Agency

SUPPLEMENTAL INFORMATION

I. General Information

A. Does this action apply to me?

Entities affected by this action include sources in all sectors of the economy, including commercial and residential sources. Entities potentially affected by this action also include States, local permitting authorities, and tribal authorities. The majority of categories and entities potentially affected by this action are expected to be in the following groups:
Industry group NAICS \a\ Agriculture, fishing, and hunting...... 11.
Mining................................. 21.
Utilities (electric, natural gas, other 2211, 2212, 2213.
systems).
Manufacturing (food, beverages, 311, 312, 313, 314, 315, 316. tobacco, textiles, leather).
Wood product, paper manufacturing...... 321, 322.
Petroleum and coal products 32411, 32412, 32419. manufacturing.
Chemical manufacturing................. 3251, 3252, 3253, 3254, 3255, 3256, 3259.
Rubber product manufacturing........... 3261, 3262.
Miscellaneous chemical products........ 32552, 32592, 32591, 325182, 32551.
Nonmetallic mineral product 3271, 3272, 3273, 3274, 3279. manufacturing.
Primary and fabricated metal 3311, 3312, 3313, 3314, 3315, manufacturing. 3321, 3322, 3323, 3324, 3325, 3326, 3327, 3328, 3329. Machinery manufacturing................ 3331, 3332, 3333, 3334, 3335, 3336, 3339.
Computer and electronic products 3341, 3342, 3343, 3344, 3345, manufacturing. 4446.
Electrical equipment, appliance, and 3351, 3352, 3353, 3359. component manufacturing.
Transportation equipment manufacturing. 3361, 3362, 3363, 3364, 3365, 3366, 3366, 3369. Furniture and related product 3371, 3372, 3379.
manufacturing.
Miscellaneous manufacturing............ 3391, 3399.
Waste management and remediation....... 5622, 5629.
Hospitals/Nursing and residential care 6221, 6231, 6232, 6233, 6239. facilities.
Personal and laundry services.......... 8122, 8123.
Residential/private households......... 8141.
NonResidential (Commercial)........... Not available. Codes only exist for private households, construction, and leasing/ sales industries. \a\ North American Industry Classification System.

B. How is this preamble organized?

The information presented in this preamble is organized as follows: Outline
I. General Information

A. Does this action apply to me?

B. How is this preamble organized?

C. Preamble Acronyms and Abbreviations
II. Overview of the Final Rule
III. Background

A. What are GHGs and their sources?

B. Endangerment Finding and the LDVR

1. Endangerment Finding

2. LightDuty Vehicle Rule

C. What are the general requirements of the PSD program?

1. Overview of the PSD Program

2. General Requirements for PSD

D. What are the general requirements of the Title V operating permits program?

1. Overview of Title V

2. Title V Permit Requirements

E. The Interpretive Memo
IV. Summary of Final Actions

[[Page 31515]]

A. How do you define the GHG pollutant for PSD and Title V purposes?

1. GHG Pollutant Defined as the SumofSix WellMixed GHGs

2. What GWP values should be used for calculating CO2e?

B. When will PSD and Title V applicability begin for GHGs and emission sources?

1. What are the Step 1 thresholds, timing, and calculation methodology?

2. What are the Step 2 thresholds, timing, and calculation methodology?

3. What about Step 3?

4. What about the proposed 6year exclusion for smaller sources?

5. When and how will EPA take further action on smaller sources?

C. How do state, local, and tribal area programs adopt the final GHG applicability thresholds?

D. How do you treat GHGs for purposes of Title V permit fees?

E. Other Actions and Issues

1. Timing for Permit Streamlining Techniques

2. Guidance for BACT Determinations

3. Requests for Higher CategorySpecific Thresholds and Exemptions From Applicability

4. Transitional Issues Including Requests for Grandfathering V. What is the legal and policy rationale for the final actions?

A. Rationale for Our Approach to Calculating GHG Emissions for PSD and Title V Applicability Purposes

1. Grouping of GHGs Into a Single Pollutant

2. Identifying Which GHGs Are Included in the Group

3. Use of GWP vs. MassBased GHG Thresholds

4. Determining What GWP Values Are To Be Used

5. Use of Short Tons vs. Metric Tons

B. Rationale for Thresholds and Timing for PSD and Title V Applicability to GHG Emissions Sources

1. Overview

2. Data Concerning Costs to Sources and Administrative Burdens to Permitting Authorities

3. ``Absurd Results,'' ``Administrative Necessity,'' and ``One StepataTime'' Legal Doctrines

4. The PSD and Title V Programs

5. Application of the ``Absurd Results'' Doctrine for the PSD Program

6. Application of the ``Absurd Results'' Doctrine for the Title V Program

7. Additional Rulemaking for the PSD and Title V Programs

8. Rationale for the Phasein Schedule for Applying PSD and Title V to GHG Sources

9. ``Administrative Necessity'' Basis for PSD and Title V Requirements in Tailoring Rule

10. ``OneStepataTime'' Basis for Tailoring Rule

C. Mechanisms for Implementing and Adopting the Tailoring Approach

1. PSD Approach: Background and Proposal

2. Rationale for Our Final Approach to Implementing PSD

3. Other Mechanisms

4. Codification of Interpretive Memo

5. Delaying Limited Approvals and Request for Submission of Information From States Implementing a SIPApproved PSD Program

6. Title V Programs

D. Rationale for Treatment of GHGs for Title V Permit Fees

E. Other Actions and Issues

1. Permit Streamlining Techniques

2. Guidance for BACT Determinations

3. Requests for Higher CategorySpecific Thresholds or Exemptions From Applicability

4. Transitional Issues Including Requests for Grandfathering VI. What are the economic impacts of the final rule?

A. What entities are affected by this final rule?

B. What are the estimated annual benefits to sources due to regulatory relief from the statutory requirements?

1. What are annual estimated benefits or avoided burden costs for title V permits?

2. What are annual benefits or avoided costs associated with NSR permitting regulatory relief?

C. What are the economic impacts of this rulemaking?

D. What are the costs of the final rule for society?

E. What are the net benefits of this final rule? VII. Comments on Statutory and Executive Order Reviews

A. Comments on Executive Order 12866Regulatory Planning and Review

B. Comments on the Paperwork Reduction Act

C. Comments on the RFA

D. Comments on the Unfunded Mandates Reform Act

E. Comments on Executive Order 13132Federalism

F. Comments on Executive Order 13175Consultation and Coordination With Indian Tribal Governments

G. Comments on Executive Order 13211Actions That Significantly Affect Energy Supply, Distribution, or Use

VIII. Statutory and Executive Order Reviews

A. Executive Order 12866Regulatory Planning and Review

B. Paperwork Reduction Act

C. Regulatory Flexibility Act

D. Unfunded Mandates Reform Act

E. Executive Order 13132Federalism

F. Executive Order 13175Consultation and Coordination With Indian Tribal Governments

G. Executive Order 13045Protection of Children From Environmental Health and Safety Risks

H. Executive Order 13211Actions That Significantly Affect Energy Supply, Distribution, or Use

I. National Technology Transfer and Advancement Act

J. Executive Order 12898Federal Actions To Address Environmental Justice in Minority Populations and LowIncome Populations

K. Congressional Review Act

L. Judicial Review
IX. Statutory Authority

C. Preamble Acronyms and Abbreviations

The following are abbreviations of terms used in this preamble. ANPR Advance Notice of Proposed Rulemaking
APA Administrative Procedure Act
AQRVs Air Quality Related Values
BACT Best Available Control Technology
Btu British thermal units
Btu/hr British thermal units per hour
CAA or Act Clean Air Act
CAAAC Clean Air Act Advisory Committee
CAFE Corporate Average Fuel Economy
CH4 Methane
CO Carbon Monoxide
CO2 Carbon Dioxide
CO2e Carbon Dioxide Equivalent
EPA U.S. Environmental Protection Agency
FDA Food and Drug Administration
FIP Federal Implementation Plan
FTEs FullTime Equivalents
GHG Greenhouse Gas
GHz Gigahertz
GWP Global Warming Potential
HAP Hazardous Air Pollutant
HFCs Hydrofluorocarbons
ICR Information Collection Request
IPCC Intergovernmental Panel on Climate Change
LDVR LightDuty Vehicle Rule
MACT Maximum Achievable Control Technology
MCL Maximum Contaminant Level
N2O Nitrous Oxide
NAAQS National Ambient Air Quality Standard
NHTSA National Highway Traffic Safety Administration
NMOC Nonmethane Organic Compounds
NOX Nitrogen Oxides
NPDES National Pollutant Discharge Elimination System
NSPS New Source Performance Standard
NSR New Source Review
NTAA National Tribal Air Association
NTTAA National Technology Transfer and Advancement Act
OMB Office of Management and Budget
PFCs Perfluorocarbons
PM Particulate Matter
PSD Prevention of Significant Deterioration
PTE Potential to Emit
RFA Regulatory Flexibility Act
RIA Regulatory Impact Analysis
RTC Response to Comment
SBA Small Business Administration
SBAR Small Business Advocacy Review
SBREFA Small Business Regulatory Enforcement Fairness Act
SF6 Sulfur Hexafluoride
SIP State Implementation Plan
SNPR Supplemental Notice of Proposed Rulemaking
TIP Tribal Implementation Plan
TRS Total Reduced Sulfur
TSD Technical Support Document
tpy Tons Per Year
UMRA Unfunded Mandates Reform Act
UNFCCC United Nations Framework Convention on Climate Change VOC Volatile Organic Compound
[[Page 31516]]

II. Overview of the Final Rule

EPA is relieving overwhelming permitting burdens that would, in the absence of this rule, fall on permitting authorities and sources. We accomplish this by tailoring the applicability criteria that determine which GHG emission sources become subject to the PSD and title V programs \1\ of the CAA. In particular, EPA is establishing with this rulemaking a phasein approach for PSD and title V applicability, and is establishing the first two steps of the phasein for the largest emitters of GHGs. We also commit to certain followup actions regarding future steps beyond the first two, discussed in more detail later. Our legal basis for this rule is our interpretation of the PSD and title V applicability provisions under the familiar Chevron \2\ twostep framework for interpreting administrative statutes, taking account of three legal doctrines, both separately and interdependently: They are what we will call (1) The ``absurd results'' doctrine, which authorizes agencies to apply statutory requirements differently than a literal reading would indicate, as necessary to effectuate congressional intent and avoid absurd results, (2) the ``administrative necessity'' doctrine, which authorizes agencies to apply statutory requirements in a way that avoids impossible administrative burdens; and (3) the ``one stepatatime'' doctrine, which authorizes agencies to implement statutory requirements a step at a time. This legal basis justifies each of the actions we take with this rulee.g., each of the first two steps of the phasein approachboth (1) as part of the overall tailoring approach, and (2) independently of each other action we take with this rule. EPA also has authority for this Tailoring Rule under CAA section 301(a)(1), which authorizes the Administrator ``to prescribe such regulations as are necessary to carry out his functions under [the CAA].''
\1\ Unless otherwise indicated, references in this preamble to ``title V,'' ``title V requirements,'' the ``title V program,'' and similar references are to the operating permit provisions in CAA sections 501506, and not the ``small business stationary source technical and environmental compliance assistance program'' under CAA section 507.

\2\ Chevron U.S.A. Inc. v. NRDC, 467 U.S. 837 (1984).

For the first step of this Tailoring Rule, which will begin on January 2, 2011, PSD or title V requirements will apply to sources' GHG emissions only if the sources are subject to PSD or title V anyway due to their nonGHG pollutants. Therefore, EPA will not require sources or modifications to evaluate whether they are subject to PSD or title V requirements solely on account of their GHG emissions. Specifically, for PSD, Step 1 requires that as of January 2, 2011, the applicable requirements of PSD, most notably, the best available control technology (BACT) requirement, will apply to projects that increase net GHG emissions by at least 75,000 tpy carbon dioxide equivalent (CO2e), but only if the project also significantly increases emissions of at least one nonGHG pollutant. For the title V program, only existing sources with, or new sources obtaining, title V permits for nonGHG pollutants will be required to address GHGs during this first step.

The second step of the Tailoring Rule, beginning on July 1, 2011, will phase in additional large sources of GHG emissions. New sources as well as existing sources not already subject to title V that emit, or have the potential to emit, at least 100,000 tpy CO2e will become subject to the PSD and title V requirements. In addition, sources that emit or have the potential to emit at least 100,000 tpy CO2e and that undertake a modification that increases net emissions of GHGs by at least 75,000 tpy CO2e will also be subject to PSD requirements. For both steps, we also note that if sources or modifications exceed these CO2eadjusted GHG triggers, they are not covered by permitting requirements unless their GHG emissions also exceed the corresponding massbased triggers (i.e., unadjusted for CO2e.)

EPA believes that the costs to the sources and the administrative burdens to the permitting authorities of PSD and title V permitting will be manageable at the levels in these initial two steps, and that it would be administratively infeasible to subject additional sources to PSD and title V requirements at those times. However, we also intend to issue a supplemental notice of proposed rulemaking (SNPR) in 2011, in which we will propose or solicit comment on a third step of the phasein that would include more sources, beginning by July 1, 2013. In the same rulemaking, we may propose or solicit comment on a permanent exclusion from permitting for some category of sources, based on the doctrine of ``absurd results,'' within the Chevron framework. We are establishing an enforceable commitment that we will complete this rulemaking by July 1, 2012, which will allow for 1 year's notice before Step 3 would take effect.

In addition, we commit to explore streamlining techniques that may well make the permitting programs much more efficient to administer for GHGs, and that therefore may allow their expansion to smaller sources. We expect that the initial streamlining techniques will take several years to develop and implement.

We are also including in this action a rule that no source with emissions below 50,000 tpy CO2e, and no modification resulting in net GHG increases of less than 50,000 tpy CO2e, will be subject to PSD or title V permitting before at least 6 years from now, April 30, 2016. This is because we are able to conclude at the present time that the administrative burdens that would accompany permitting sources below this level will be so great that even the streamlining actions that EPA may be able to develop and implement in the next several years, and even with the increases in permitting resources that we can reasonably expect the permitting authorities to acquire, it will be impossible to administer the permit programs for these sources until at least 2016.

Further, we are establishing an enforceable commitment that we will (1) Complete a study by April 30, 2015, to evaluate the status of PSD and title V permitting for GHGemitting sources, including progress in developing streamlining techniques; and (2) complete further rulemaking based on that study by April 30, 2016, to address the permitting of smaller sources. That rulemaking may also consider additional permanent exclusions based on the ``absurd results'' doctrine, where applicable.

This Tailoring Rulemaking is necessary because without it, PSD and title V would apply to all stationary sources that emit or have the potential to emit more than 100 or 250 tons of GHGs per year beginning on January 2, 2011. This is the date when EPA's recently promulgated LightDuty Vehicle Rule (LDVR) takes effect, imposing control requirements for the first time on carbon dioxide (CO2) and other GHGs. If this January 2, 2011 date were to pass without this Tailoring Rule being in effect, PSD and title V requirements would apply at the 100/250 tpy applicability levels provided under a literal reading of the CAA as of that date. From that point forward, a source owner proposing to construct any new major source that emits at or higher than the applicability levels (and which therefore may be referred to as a ``major'' source) or modify any existing major source in a way that would increase GHG emissions would need to obtain a permit under the PSD program that addresses these emissions before construction or modification could begin. Similarly, title V would apply to a new or existing source exceeding the 100 tpy
[[Page 31517]]
applicability level in the Act, if the source did not already have a title V permit.

Under these circumstances, many small sources would be burdened by the costs of the individualized PSD control technology requirements and permit applications that the PSD provisions, absent streamlining, require. Additionally, state and local permitting authorities would be burdened by the extraordinary number of these permit applications, which are orders of magnitude greater than the current inventory of permits and would vastly exceed the current administrative resources of the permitting authorities. Permit gridlock would result with the permitting authorities able to issue only a tiny fraction of the permits requested.

These impactsthe costs to sources and administrative burdens to permitting authoritiesthat would result from application of the PSD and title V programs for GHG emissions at the statutory levels as of January 2, 2011, are so severe that they bring the judicial doctrines of ``absurd results,'' ``administrative necessity,'' and ``onestepat atime'' into the Chevron twostep analytical framework for statutes administered by agencies. Under the U.S. Supreme Court's decision in Chevron, the agency must, at Step 1, determine whether Congress's intent as to the specific matter at issue is clear, and, if so, the agency must give effect to that intent.\3\ If congressional intent is not clear, then, at Step 2, the agency has discretion to fashion an interpretation that is a reasonable construction of the statute. \3\ Chevron U.S.A. Inc. v. NRDC, 467 U.S. 837, 84243 (1984).

To determine congressional intent, the agency must first consider the words of the statutory requirements, and if their literal meaning answers the question at hand, then, in most cases, the agency must implement those requirements by their terms. However, under the ``absurd results'' doctrine, the literal meaning of statutory requirements should not be considered to indicate congressional intent if that literal meaning would produce a result that is senseless or that is otherwise inconsistent withand especially one that underminesunderlying congressional purpose. In these cases, if congressional intent for how the requirements apply to the question at hand is clear, the agency should implement the statutory requirements not in accordance with their literal meaning, but rather in a manner that most closely effectuates congressional intent. If congressional intent is not clear, then an agency may select an interpretation that is reasonable under the statute.

Under the ``administrative necessity'' doctrine, Congress is presumed, at Chevron Step 1, to intend that its statutory directives to agencies be administrable, and not to have intended to have written statutory requirements that are impossible to administer. Therefore, under this doctrine, an agency may depart from statutory requirements that, by their terms, are impossible to administer, but the agency may depart no more than necessary to render the requirements administrable. Under the ``onestepatatime'' doctrine, Congress is presumed at Chevron Step 1 to have intended to allow the agency to administer the statutory requirements on a stepbystep basis, as appropriate, when the agency remains on track to implement the requirements as a whole. Each of these doctrines supports our action separately, but the three also are intertwined and support our action in a comprehensive manner.

Here, we have determined, through analysis of burden and emissions data as well as consideration of extensive public comment, that the costs to sources and administrative burdens to permitting authorities that would result from application of the PSD and title V programs for GHG emissions at the statutory levels as of January 2, 2011 should be considered ``absurd results.'' Therefore, we conclude that under the ``absurd results'' doctrine, Congress could not have intended that the PSD or title V applicability provisionsin particular, the threshold levels and timing requirementsapply literally to GHG sources as of that date.

Even so, the PSD and title V provisions and their legislative history do indicate a clear congressional intent, under Chevron Step 1, as to whether the two permitting programs applied to GHG sources, and that the intent was in the affirmative, that the permitting programs do apply to GHG sources. Our previous regulatory action defining the applicability provisions made this clear, and we do not reopen this issue in this rulemaking. Moreover, even if this longestablished regulatory position were not justifiable based on Chevron Step 1on the grounds that in fact, congressional intent on this point is not clearthen we believe that this position, that the statutory provisions to apply PSD and title V generally to GHG sources, was justified under Chevron step 2.\4\
\4\ In this preamble and the response to comments document we fully address arguments that commenters and others have presented about congressional intent and coverage of GHGs. We do so to be fully responsive, even though we believe that this is a settled matter for which the time for judicial review has passed.

As to how to apply the PSD program to GHG sources, congressional intent, as expressed in the various statutory provisions and statements in the legislative history, is clear that PSD should apply at least to the largest sources initially, at least to as many more sources as possible and as promptly as possible over timeconsistent with streamlining actions that we intend to consider coupled with increases in permitting authority resourcesand at least to a certain point. This is the approach we take in this Tailoring Rule, and because it is consistent with congressional intent, we believe it is required under Chevron Step 1. Even if congressional intent were not clear as to how to apply the PSD requirements to GHG sources, we would have authority under Chevron Step 2 to establish a reasonable interpretation that is consistent with the PSD provisions, and we believe that the tailoring approach so qualifies.

As for title V, the statutory provisions and legislative history, which of course are different than those concerning the PSD program, do not express a clear intent as to how title V applies to GHG sources, which leads our analysis to Chevron Step 2, and here, again, we believe that the tailoring approach is a reasonable interpretation that is consistent with the title V provisions.

For both PSD and title V, we intend to use the tailoring approach to address smaller GHG sources over time, consistent with Congress's expectations that the programs would not impose undue costs to sources or undue administrative burdens to permitting authorities. However, we cannot say at this point how close to the statutory thresholds we will eventually reach. Because this rule establishes only the first two phases of the tailoring approach, we do not find it necessary to answer these questions in this rule, and instead we expect to resolve them through future rulemaking. We will remain mindful of the concerns that Congress expressed about including small sources in either program. We intend to consider the issue of the applicability of title V to GHG sources without applicable requirements (i.e., ``empty permits'') in future steps of our tailoring approach. When we do so, we will further assess the potential for the approach of excluding empty permits from title V to relieve burden consistent with statutory requirements.

In addition, because Congress can be said to have intended the PSD and title
[[Page 31518]]
V programs to apply to GHG sources, the Tailoring Rule is also justifiable under the ``administrative necessity'' and ``onestepata time'' doctrines.

The legal analysis just described justifies each of the actions in this rule. The first two steps that we promulgate in this rule, which take effect on January 2, 2011 and July 1, 2011, constitute the most that permitting authorities can reasonably be expected to do by those times. Similarly, the 50,000 tpy floor that we promulgate through at least April 30, 2016 is reasonable because the information we have available now shows that it constitutes the most that permitting authorities can reasonably be expected to do by that date. Finally, the study and two additional rulemakingsto take effect by July 1, 2013 and April 30, 2016to which we commit in this rule establish a track for acquiring additional information and for taking further steps to address the application of PSD and title V more closely to the literal statutory levels. We intend to apply them as closely to those levels as is consistent with congressional intent and administrative imperatives, in light of the ``absurd results,'' ``administrative necessity,'' and ``onestepatatime'' doctrines, although, as noted previously, we will consider in future rulemaking how closely to the statutory thresholds we will be able to implement the PSD and title V programs as well as what to require with respect to a potentially large number of sources with empty title V permits.

In this rule, we are adopting regulatory language codifying our phasein approach. As we will explain, many state, local and tribal area programs will likely be able to immediately implement our approach without rule or statutory changes by, for example, interpreting the term ``subject to regulation'' that is part of the applicability provisions for PSD and title V. We ask permitting authorities to confirm that they will follow this implementation approach for their programs, and if they cannot, then we ask them to notify us so that we can take appropriate followup action to narrow our federal approval of their programs before GHGs become subject to regulation for PSD and title V programs on January 2, 2011. Narrowing our approval will ensure that for federal purposes, GHG sources below the size thresholds we establish in this Tailoring Rule are not obligated to hold PSD or title V permits until the states develop and submit revised PSD and title V programs that EPA approves, either because they adopt our tailoring approach or because, if they continue to cover smaller GHG sources, the states have demonstrated that they have adequate resources to administer those programs.

The thresholds we are establishing are based on CO2e for the aggregate sum of six greenhouse gases that constitute the pollutant that will be subject to regulation, which we refer to as GHGs.\5\ These gases are: CO2, methane (CH4), nitrous oxide (N2O), hydrofluorocarbons (HFCs), perfluorocarbons (PFCs), and sulfur hexafluoride (SF6). Thus, in this rule, we provide that PSD and title V applicability is based on the quantity that results when the mass emissions of each of these gases is multiplied by the Global Warming Potential (GWP) of that gas, and then summed for all six gases. However, we further provide that in order for a source's GHG emissions to trigger PSD or title V requirements, the quantity of the GHGs must equal or exceed both the applicability thresholds established in this rulemaking on a CO2e basis and the statutory thresholds of 100 or 250 tpy on a mass basis.\6\ Similarly, in order for a source to be subject to the PSD modification requirements, the source's net GHG emissions increase must exceed the applicable significance level on a CO2e basis and must also result in a net mass increase of the constituent gases combined. \5\ The term ``greenhouse gases'' is commonly used to refer generally to gases that have heattrapping properties. However, in this notice, unless noted otherwise, we use it to refer to specifically to the pollutant regulated in the LDVR.
\6\ The relevant thresholds are 100 tpy for title V, and 250 tpy for PSD, except for 28 categories listed in EPA regulations for which the PSD threshold is 100 tpy.

We are adopting this rule after careful consideration of numerous public comments. On October 27, 2009 (74 FR 55292), EPA proposed the GHG Tailoring Rule. EPA held two public hearings on the proposed rule, and received over 400,000 written public comments. The public comment period ended on December 28, 2009. The comments have provided detailed information that has helped EPA understand better the issues and potential impacts of this rule, and the final rule described in this preamble incorporates many of the suggestions we received. We respond to many of these comments in explaining our rationale for the final rule, which is described in section V. The final rule adopts many elements of the proposal but differs from the proposal in several important respects. We proposed to apply PSD and title V to GHG sources that emit or have the potential to emit at least 25,000 tpy CO2e, and we proposed a PSD significance level in a range between 10,000 and 25,000 tpy CO2e, but based on consideration of the additional information we received and our further analysis, we are finalizing the threshold levels in the amounts and on the schedule described previously. In addition, the mechanism for state, local, and tribal program implementation has been significantly changed to reflect the comments received that we needed to develop an implementation approach that states could adopt under state law more expeditiously.

The remainder of this notice describes our approach and rationale in more detail. Following this overview, section III of this preamble provides background information on the nature of GHG emissions, recent regulatory developments that affect when and how GHG emissions are subject to stationary source permitting, and the general requirements of the PSD and title V programs. Section IV describes in detail the summary of the key actions being taken in this rule, including the determination of emissions, the thresholds and timing for the phasein, our approach to implementing the phasein, and the additional future actions we will take. Section V provides a more detailed description of each action, explaining the policy and legal rationale and responding to comments received. Section V begins with our decisions on how to calculate the massbased and CO2ebased emissions used in the phasein. Section V then turns to our legal and policy rationale for the first two steps of the phasein, the 50,000 tpy floor, and the subsequent study and rulemakings to determine whether and how smaller sources should be subject to permitting. This section then describes key implementation issues including the approach to state adoption. After describing our plans for followup on title V fee programs, the section concludes by describing permit streamlining techniques; guidance on BACT for the GHG sources that are affected under the first two steps of the Tailoring Rule phasein; requests for exemptions; and transitional issues, including grandfathering. Finally, section VI describes the expected impacts that will result from the phasein approach (i.e., the narrower application of PSD and title V requirements during the phasein period) and sections VII and VIII address administrative requirements.
III. Background

A. What are GHGs and their sources?

Greenhouse gases trap the Earth's heat that would otherwise escape from the atmosphere into space, and form the
[[Page 31519]]
greenhouse effect that helps keep the Earth warm enough for life. Greenhouse gases are naturally present in the atmosphere and are also emitted by human activities. Human activities are intensifying the naturally occurring greenhouse effect by increasing the amount of GHGs in the atmosphere, which is changing the climate in a way that endangers human health, society, and the natural environment.

Some GHGs, such as CO2, are emitted to the atmosphere through natural processes as well as human activities. Other gases, such as fluorinated gases, are created and emitted solely through human activities. As previously noted, the wellmixed GHGs of concern directly emitted by human activities include CO2, CH4, N2O, HFCs, PFCs, and SF6. These six GHGs will, for the purposes of this final rule, be referred to collectively as ``the six wellmixed GHGs,'' or, simply, GHGs, and together constitute the ``air pollutant'' upon which the GHG thresholds in this action are based. These six gases remain in the atmosphere for decades to centuries where they become wellmixed globally in the atmosphere. When they are emitted more quickly than natural processes can remove them from the atmosphere, their concentrations increase, thus increasing the greenhouse effect. The heating effect caused by the humaninduced buildup of GHGs in the atmosphere is very likely the cause of most of the observed global warming over the last 50 years. A detailed explanation of greenhouse gases, climate change and its impact on health, society, and the environment is included in EPA's technical support document (TSD) for the endangerment finding final rule (Docket ID No. EPAHQOAR2009047211292).

In the United States, the combustion of fossil fuels (e.g., coal, oil, gas) is the largest source of CO2 emissions and accounts for 80 percent of the total GHG emissions. Anthropogenic CO2 emissions released from a variety of sources, including through the use of fossil fuel combustion and cement production from geologically stored carbon (e.g., coal, oil, and natural gas) that is hundreds of millions of years old, as well as anthropogenic CO2 emissions from landuse changes such as deforestation, perturb the atmospheric concentration of CO2 and the distribution of carbon within different reservoirs readjusts. More than half of the energy related emissions come from large stationary sources such as power plants, while about a third comes from transportation. Of the six wellmixed GHGs, four (CO2, CH4, N2O, and HFCs) are emitted by motor vehicles. In the United States industrial processes (such as the production of cement, steel, and aluminum), agriculture, forestry, other land use, and waste management are also important sources of GHGs.

Different GHGs have different heattrapping capacities. The concept of GWP was developed to compare the heattrapping capacity and atmospheric lifetime of one GHG to another. The definition of a GWP for a particular GHG is the ratio of heat trapped by one unit mass of the GHG to that of one unit mass of CO2 over a specified time period. When quantities of the different GHGs are multiplied by their GWPs, the different GHGs can be summed and compared on a
CO2e basis. For example, CH4 has a GWP of 21, meaning each ton of CH4 emissions would have 21 times as much impact on global warming over a 100year time horizon as 1 ton of CO2 emissions. Thus, on the basis of heattrapping capability, 1 ton of CH4 would equal 21 tons of CO2e. The GWPs of the nonCO2 GHGs range from 21 (for CH4) up to 23,900 (for SF6). Aggregating all GHGs on a CO2e basis at the source level allows a facility to evaluate its total GHG emissions contribution based on a single metric.
B. Endangerment Finding and the LDVR

1. Endangerment Finding

On April 2, 2007, the U.S. Supreme Court found that GHGs are air pollutants under CAA section 302(g). Massachusetts v. EPA, 549 U.S. 497 (2007). As a result, the Supreme Court found that EPA was required to determine, under CAA section 202(a), whether (1) GHGs from new motor vehicles cause or contribute to air pollution which may reasonably be anticipated to endanger public health or welfare, or (2) the science is too uncertain to make a reasoned decision. After issuing a proposal and receiving comment, on December 7, 2009, the Administrator signed two distinct findings regarding GHGs under CAA section 202(a):

  • Endangerment Finding: The Administrator found that the current and projected atmospheric concentrations of the mix of six longlived and directly emitted GHGsCO2, CH4, N2O, HFCs, PFCs, and SF6 (referred to as ``well mixed greenhouse gases'' in the endangerment finding)are reasonably anticipated to endanger the public health and welfare of current and future generations.
  • Cause or Contribute Finding: The Administrator found that the emissions of the single air pollutant defined as the aggregate group of six wellmixed greenhouses gases from new motor vehicles and new motor vehicle engines contributes to the GHG air pollution that threatens public health and welfare.
    These findings, which were published December 15, 2009 (74 FR 66496), do not themselves impose any requirements on industry or other entities. However, they were a prerequisite to finalizing the GHG standards for lightduty vehicles, described next.

    2. LightDuty Vehicle Rule

    The LDVR, 75 FR 25324 (May 7, 2010), is a joint rule between EPA and the Department of Transportation's National Highway Traffic Safety Administration (NHTSA) that establishes a national program consisting of new standards for lightduty vehicles that will reduce GHG emissions and improve fuel economy. EPA finalized the national GHG emissions standards under the Act, and NHTSA finalized Corporate Average Fuel Economy (CAFE) standards under the Energy Policy and Conservation Act, as amended. The new standards apply to new passenger cars, lightduty trucks, and mediumduty passenger vehicles, starting with model year 2012. The EPA GHG standards are projected to result in an estimated combined average emissions level of 250 grams of CO2 per mile for model year 2016 vehicles. The standards begin with the 2012 model year, with standards increasing in stringency through model year 2016. The standards are a fleet average for each manufacturer, based on a footprint attribute curve, meaning that the actual target for a vehicle will vary depending on the size of the vehicle. Under the footprintbased standards, each manufacturer will have a GHG standard unique to its fleet, depending on the footprints of the vehicle models produced by that manufacturer. A manufacturer will have separate footprintbased standards for cars and for trucks.

    The endangerment and contribution findings described previously require EPA to issue standards under section 202(a) ``applicable to emission'' of the air pollutant that EPA found causes or contributes to the air pollution that endangers public health and welfare. The final emissions standards satisfy this requirement for GHGs from lightduty vehicles. Under section 202(a), the Administrator has significant discretion in how to structure the standards that apply to the emission of the air pollutant at issue here, the aggregate group of six GHGs. EPA has the discretion under section 202(a) to adopt separate standards for each gas, a single
    [[Page 31520]]
    composite standard covering various gases, or any combination of these. In the LDVR, EPA finalized separate standards for N2O and CH4, and a CO2 standard that provides for credits based on reductions of HFCs, as the appropriate way to issue standards applicable to emission of the single air pollutant, the aggregate group of six GHGs. EPA did not set any standards for PFCs or SF6, as they are not emitted by motor vehicles.
    C. What are the general requirements of the PSD program?

    1. Overview of the PSD Program

    The PSD program is a preconstruction review and permitting program applicable to new major stationary sources and major modifications at existing major stationary sources. The PSD program applies in areas that are designated ``attainment'' or ``unclassifiable'' for a National Ambient Air Quality Standard (NAAQS). The PSD program is contained in part C of title I of the CAA. The ``nonattainment new source review (NSR)'' program applies in areas not in attainment of a NAAQS or in the Ozone Transport Region and is implemented under the requirements of part D of title I of the CAA. Collectively, we commonly refer to these two programs as the major NSR program. The governing EPA rules are contained in 40 CFR 51.165, 51.166, 52.21, 52.24, and part 51, Appendices S and W. There is no NAAQS for CO2 or any of the other wellmixed GHGs, nor has EPA proposed any such NAAQS; therefore, unless and until we take further such action, we do not anticipate that the nonattainment NSR program will apply to GHGs.

    The applicability of PSD to a particular source must be determined in advance of construction or modification and is pollutantspecific. The primary criterion in determining PSD applicability for a proposed source is whether the source is a ``major emitting facility,'' based on its predicted potential emissions of regulated pollutants, within the meaning of CAA section 169(1) and either constructs or undertakes a modification. EPA has implemented these requirements in its regulations, which use somewhat different terminology for determining PSD applicability, which is whether the source is a ``major stationary source'' or whether the proposed project is a ``major modification.'' a. Major Stationary Source

    Under PSD, a ``major stationary source'' is any source belonging to a specified list of 28 source categories which emits or has the potential to emit 100 tpy or more of any pollutant subject to regulation under the CAA, or any other source type which emits or has the potential to emit such pollutants in amounts equal to or greater than 250 tpy. We refer to these levels as the 100/250tpy thresholds. A new source with a potential to emit (PTE) at or above the applicable ``major stationary source threshold'' is subject to major source NSR. These limits originate from section 169 of the CAA, which applies PSD to any ``major emitting facility'' and defines the term to include any source that emits or has a PTE of 100 or 250 tpy, depending on the source category. Note that the major source definition incorporates the phrase ``subject to regulation,'' which, as described later, will begin to include GHGs on January 2, 2011, under our interpretation of that phrase discussed in the recent Interpretive Memo notice. 75 FR 17004, April 2, 2010.

    b. Major Modifications

    PSD also applies to existing sources that undertake a ``major modification,'' which occurs: (1) When there is a physical change in, or change in the method of operation of, a ``major stationary source;'' (2) the change results in a ``significant'' emission increase of a pollutant subject to regulation (equal to or above the significance level that EPA has set for the pollutant in 40 CFR 52.21(b)(23)); and (3) there is a ``significant net emissions increase'' of a pollutant subject to regulation that is equal to or above the significance level (defined in 40 CFR 52.21(b)(23)). Significance levels, which EPA has promulgated for criteria pollutants and certain other pollutants, represent a de minimis contribution to air quality problems. When EPA has not set a significance level for a regulated NSR pollutant, PSD applies to an increase of the pollutant in any amount (that is, in effect, the significance level is treated as zero).

    2. General Requirements for PSD

    This section provides a very brief summary of the main requirements of the PSD program. One principal requirement is that a new major source or major modification must apply BACT, which is determined on a casebycase basis taking into account, among other factors, the cost effectiveness of the control and energy and environmental impacts. EPA has developed a ``topdown'' approach for BACT review, which involves a decision process that includes identification of all available control technologies, elimination of technically infeasible options, ranking of remaining options by control and cost effectiveness, and then selection of BACT. Under PSD, once a source is determined to be major for any regulated NSR pollutant, a BACT review is performed for each attainment pollutant that exceeds its PSD significance level as part of new construction or for modification projects at the source, where there is a significant increase and a significant net emissions increase of such pollutant.\7\
    \7\ We note that the PSD program has historically operated in this fashion for all pollutantswhen new sources or modifications are ``major,'' PSD applies to all pollutants that are emitted in significant quantities from the source or project. This rule does not alter that for sources or modifications that are major due to their GHG emissions.

    In addition to performing BACT, the source must analyze impacts on ambient air quality to assure that no violation of any NAAQS or PSD increments will result, and must analyze impacts on soil, vegetation, and visibility. In addition, sources or modifications that would impact Class I areas (e.g., national parks) may be subject to additional requirements to protect air quality related values (AQRVs) that have been identified for such areas. Under PSD, if a source's proposed project may impact a Class I area, the Federal Land Manager is notified and is responsible for evaluating a source's projected impact on the AQRVs and recommending either approval or disapproval of the source's permit application based on anticipated impacts. There are currently no NAAQS or PSD increments established for GHGs, and therefore these PSD requirements would not apply for GHGs, even when PSD is triggered for GHGs. However, if PSD is triggered for a GHG emissions source, all regulated NSR pollutants which the new source emits in significant amounts would be subject to PSD requirements. Therefore, if a facility triggers review for regulated NSR pollutants that are nonGHG pollutants for which there are established NAAQS or increments, the air quality, additional impacts, and Class I requirements would apply to those pollutants.

    The permitting authority must provide notice of its preliminary decision on a source's application for a PSD permit, and must provide an opportunity for comment by the public, industry, and other interested persons. After considering and responding to comments, the permitting authority must issue a final determination on the construction permit. Usually NSR permits are issued by state or local air
    [[Page 31521]]
    pollution control agencies, which have their own permit programs approved by EPA in their State Implementation Plans (SIPs). In some cases, EPA has delegated its authority to issue PSD permits to the state or local agency. In other areas, EPA issues the permits under its own authority.
    D. What are the general requirements of the title V operating permits program?

    1. Overview of Title V

    The operating permit requirements under title V are intended to improve sources' compliance with other CAA requirements. The title V program is implemented through regulations promulgated by EPA, 40 CFR part 70, for programs implemented by state and local agencies and tribes, and 40 CFR part 71, for programs generally implemented by EPA.

    In summary, the title V program requires major sources (defined and interpreted by EPA to include sources that emit or have a PTE of 100 tpy of any pollutant subject to regulation) and certain other sources to apply for operating permits. Under EPA's longstanding
    interpretation, a pollutant, such as a GHG, is ``subject to regulation'' when it is subject to a CAA requirement establishing actual control of emissions. Title V generally does not add new pollution control requirements, but it does require that each permit contain all pollution control requirements or ``applicable requirements'' required by the CAA (e.g., New Source Performance Standard (NSPS), and SIP requirements, including PSD), and it requires that certain procedural requirements be followed, especially with respect to compliance with these requirements. ``Applicable requirements'' for title V purposes include stationary source requirements, but do not include mobile source requirements. Other procedural requirements include providing review of permits by EPA, states, and the public, and requiring permit holders to track, report, and annually certify their compliance status with respect to their permit requirements.

    2. Title V Permit Requirements

    This section provides a brief summary of the requirements of the title V program that are most relevant to this action. A source generally must apply for a title V permit within 1 year of first becoming subject to permittingfor new sources, this is usually within 1 year of commencing operation. The application must include, among other things, identifying information, a description of emissions and other information necessary to determine applicability of requirements and information concerning compliance with those requirements. The permitting authority uses this information to develop the source's operating permit.

    Title V permits generally contain the following elements: (1) Emissions limitations and standards to assure compliance with all applicable requirements; (2) monitoring, recordkeeping, and reporting requirements, including submittal of a semiannual monitoring report and prompt reporting of deviations from permit terms; (3) fee payment; and (4) an annual certification of certification by a responsible official. The detailed requirements are set forth at 40 CFR 70.6.

    In addition to the permit content requirements, there are procedural requirements that must be followed in issuing title V permits, including (1) Application completeness determination; (2) public notice and a 30day public comment period, including an opportunity for a public hearing, on draft permits; (3) EPA and affected state review; and (4) a statement of the legal and factual basis of the draft permit. The permitting authority must take final action (issue or deny) on the permit applications within 18 months of receipt. EPA also has 45 days from receipt of a proposed permit to object to its issuance, and citizens have 60 days after that to petition EPA to object to a permit. Permits may also need to be revised or reopened if new requirements come into effect during the permit terms or if the source makes changes that conflict with, or necessitate changes to, the current permit. Permit revisions and reopenings follow procedural requirements which vary depending on the nature of the necessary change to the permit.

    E. The Interpretive Memo

    On December 18, 2008, EPA issued a memorandum, ``EPA's Interpretation of Regulations that Determine Pollutants Covered by Federal Prevention of Significant Deterioration (PSD) Permit Program'' (known as the ``Johnson Memo'' or the ``PSD Interpretive Memo,'' and referred to in this preamble as the ``Interpretive Memo'') that set forth EPA's interpretation regarding which EPA and state actions, with respect to a previously unregulated pollutant, cause that pollutant to become ``subject to regulation'' under the Act. Whether a pollutant is ``subject to regulation'' is important for the purposes of determining whether it is covered under the federal PSD and title V permitting programs. The Interpretive Memo established that a pollutant is ``subject to regulation'' only if it is subject to either a provision in the CAA or regulation adopted by EPA under the CAA that requires actual control of emissions of that pollutant (referred to as the ``actual control interpretation''). On February 17, 2009, EPA granted a petition for reconsideration on the Interpretive Memo, and announced its intent to conduct a rulemaking to allow for public comment on the issues raised in the memorandum and on related issues. EPA also clarified that the Interpretive Memo would remain in effect pending reconsideration.

    On March 29, 2010, EPA signed a notice conveying its decision to continue applying (with one limited refinement) the Interpretive Memo's interpretation of ``subject to regulation'' (``Interpretation of Regulations that Determine Pollutants Covered by Clean Air Act Permitting Programs''). See 75 FR 17004. EPA concluded that the ``actual control interpretation'' is the most appropriate
    interpretation to apply given the policy implications. However, we refined our interpretation in one respect: we established that PSD permitting requirements apply to a newly regulated pollutant at the time a regulatory requirement to control emissions of that pollutant ``takes effect'' (rather than upon promulgation or the legal effective date of the regulation containing such a requirement). In addition, based on the anticipated promulgation of the LDVR, we stated that the GHG requirements of the vehicle rule would take effect on January 2, 2011, because that is the earliest date that a 2012 model year vehicle may be introduced into commerce. In other words, the compliance obligation under the LDVR does not occur until a manufacturer may introduce into commerce vehicles that are required to comply with GHG standards, which will begin with model year 2012 and will not occur before January 2, 2011. We also reiterated EPA's interpretation that the 100 tpy major source threshold for title V is triggered only by pollutants ``subject to regulation'' under the Act, and we defined and applied that term for title V purposes in the same way that we did for PSD purposes. That is, we stated that a pollutant is ``subject to regulation'' if it is subject to a CAA requirement establishing ``actual control of emissions;'' that a pollutant is considered ``subject to regulation'' for title V purposes when such a requirement ``takes effect''; and, based on the anticipated promulgation of the LDVR, that the GHG requirements of the
    [[Page 31522]]

    vehicle rule would take effect on January 2, 2011.

    On April 1, 2010, we finalized the LDVR as anticipated, confirming that manufacturer certification can occur no earlier than January 2, 2011. Thus, under the terms of the final notice for the Interpretive Memo, GHGs become subject to regulation on that date, and PSD and title V program requirements will also begin to apply upon that date. IV. Summary of Final Actions

    This section describes the specific actions we are taking in this final rule. It describes the overall tailoring approach for NSR and title V applicability, the steps we are taking to put it into place, and future actions that we commit to take. The next section, V, provides the legal and policy rationale for these actions. In that section, we provide a description of our rationale and response to comments for each action, presented in the same order as we describe the actions here.
    A. How do you define the GHG pollutant for PSD and title V purposes? 1. GHG Pollutant Defined as the SumofSix WellMixed GHGs

    We are identifying the air pollutant for purposes of PSD and title V applicability to be the pollutant subject to regulation, which is the air pollutant for GHGs identified in EPA's LDVR, as well as EPA's endangerment and contribution findings.\8\ In the LDVR, EPA set emissions standards under section 202(a) that were ``applicable to emission'' of a single air pollutant defined as the aggregate sum of six GHGs. The six GHGs, which are wellmixed gases in the atmosphere, are CO2, CH4, N2O, HFCs, PFCs, and SF6. Earlier, EPA made the contribution finding for this single air pollutant.

    \8\ See 74 FR 66496, 66499, 665367. December 15, 2009.

    Furthermore, as proposed, we are using an emissions threshold that allows all six constituent gases to be evaluated using a common metricCO2e. Thus, to determine applicability, a source's GHG emissions are calculated on a CO2e basis by multiplying the mass emissions of any of the six GHGs that the source emits by that gas's GWP and then summing the CO2e for each GHG emitted by the source. This sum, expressed in terms of tpy CO2e, is then compared to the applicable CO2ebased permitting threshold to determine whether the source is subject to PSD and title V requirements.

    In addition, because we are implementing this phasein through the term ``subject to regulation,'' the regulatory language is structured such that the statutory massbased thresholds (i.e., for PSD, 100/250 tpy for new construction and zero tpy for modifications at a major stationary source, and for title V, 100 tpy) continue to apply. As a result, stationary source apply and stationary sources or modifications that do not meet these thresholds are not subject to permitting requirements. While technically evaluation of the massbased thresholds is the second step in the applicability analysis, from a practical standpoint most sources are likely to treat this as an initial screen, so that if they would not trigger PSD or title V on a mass basis, they would not proceed to evaluate emissions on a CO2e basis. We have treated evaluation of massbased thresholds as the initial step in our descriptions. As applicable, a source would evaluate these mass based thresholds by summing each of the six GHGs it emits on a mass basis (i.e., before applying GWP). We expect that it will be very rare for a new stationary source or modification to trigger permitting based on CO2e and not also trigger based on mass alone.

    Determining permit program applicability for the GHG ``air pollutant'' by using the sumofsix GHGs is based on EPA's
    interpretation that the PSD and title V requirements apply to each ``air pollutant'' that is ``subject to regulation'' under another provision of the CAA. As discussed previously, the final LDVR for GHGs makes it clear that the emissions standards EPA adopted are standards applicable to emission of the single air pollutant defined as the aggregate mix of these six wellmixed GHGs. See LDVR, May 7, 2010, 75 FR 2539899, section III.A.2.c, and 40 CFR 86.181812.\9\ For reasons explained in more detail in section V, we have determined it is legally required, and preferable from a policy standpoint, for EPA to use the same definition of the air pollutant for permitting purposes as that used in the rule that establishes the control requirements for the pollutant. We also believe there are implementation advantages for applying PSD and title V in this way. Thus, this rule establishes that a stationary source will use the group of six constituent gases for permitting applicability, rather than treating each gas individually. Similarly, you will include all six constituent gases because that is how the air pollutant is defined, even though motor vehicles only emit four of the six.
    \9\ 40 CFR 86.181812(a).
    2. What GWP values should be used for calculating CO2e?

    We are requiring that wherever you perform an emissions calculations involving CO2e for the purposes of determining the applicability of PSD or title V requirements, you use the GWP values codified in the EPA's mandatory GHG reporting rule.\10\ This approach will assure consistency between the values required for calculations under the reporting rule and for PSD or title V. In addition, because any changes to Table A1 of the mandatory GHG reporting rule regulatory text must go through a rulemaking, this approach will assure that the values used for the permitting programs will reflect the latest values adopted for usage by EPA after notice and comment.
    \10\ Table A1 to subpart A of 40 CFR part 98Global Warming Potentials, 74 FR 56395.
    B. When will PSD and title V applicability begin for GHGs and emission sources?

    Overview

    In this action, we establish the first two phases of our phasein approach, which we refer to as Steps 1 and 2. We also commit to a subsequent rulemaking in which we will propose or solicit comment on establishing a further phasein, that is, a Step 3, that would apply PSD and title V to additional sources, effective July 1, 2013, and on which we commit to take final action, as supported by the record,\11\ by no later than July 1, 2012.
    \11\ Although we commit to propose or solicit comment on lower thresholds and to take final action on that proposal by July 1, 2012, we cannot, at present, commit to promulgate lower thresholds. It will not be until the Step 3 rulemaking itself that we will gather and analyze data and receive comments that determine whether we have basis for promulgating lower thresholds.

    We also commit to undertaking an assessment of sources' and permitting authorities' progress in implementing PSD and title V for GHG sources, and to complete this assessment by 2015. We further commit to completing another round of rulemaking addressing smaller sources by April 30, 2016. Our action in that rulemaking would address permitting requirements for smaller sources, taking into account the remaining problems concerning costs to sources and burdens to permitting authorities. Finally, we determine in this action that we will apply PSD or title V requirements to sources that emit GHGs, or that conduct modifications that result in increases in emissions of GHGs, in amounts of less than 50,000 tpy CO2e any earlier than when we take the required further action to address smaller sources by April 30, 2016.

    [[Page 31523]]

    Through this process, we will implement the phasein approach by applying PSD and title V at threshold levels that are as close to the statutory levels as possible, and do so as quickly as possible, at least to a certain point. The level and timing of the thresholds that we promulgate in future actions will be based on our assessment of the resulting costs to sources and burdens to permitting authorities, and that, in turn, will depend on such variables as our progress in developing streamlining approaches and on permitting authorities' progress in developing permitting expertise and acquiring more resources. At this time, we cannot foresee exactly when or in what manner those developments will occur. Therefore, we cannot promulgate more components of the tailoring approach beyond what we promulgate in this action. We can say only that we may continue the phasein process with further rulemaking after 2016. Alternatively, we may make a definitive determination in one of the future rulemaking actions that, under the ``absurd results'' doctrine, PSD or title V applies only to c

    FOR FURTHER INFORMATION CONTACT

    Mr. Joseph Mangino, Air Quality Policy Division, Office of Air Quality Planning and Standards (C50403), Environmental Protection Agency, Research Triangle Park, NC 27711; telephone number: (919) 5419778; fax number: (919) 5415509; email address: mangino.joseph@epa.gov.